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EC number: 200-143-0 | CAS number: 52-51-7
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption
- Remarks:
- adsorption
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study conducted in accordance with GLP.
- Qualifier:
- according to guideline
- Guideline:
- other: EPA Pesticide assessment Guideline 163-1
- GLP compliance:
- yes
- Type of method:
- batch equilibrium method
- Media:
- soil
- Radiolabelling:
- yes
- Analytical monitoring:
- yes
- Details on matrix:
- SOILS
- The following soils were used in the study:
(1) Sand (Colorado, USA) supplied by Compliance Services International, Tacoma, WA, USA and received by IRI on 17 December 1990
(2) Loamy sand (Georgia, USA) supplied by Landis International Inc., Valdosta, GA, USA and received by IRI on 5 February 1991
(3) Loam (Scotland, UK) supplied by the Scottish Agricultural College, Auchincruive, Scotland and received by IRI on 31 January 1991
(4) Clay loam (Scotland, UK) supplied by the Scottish Agricultural College and received by IRI on 31 January 1991
SOIL PREPARATION
On arrival at IRI, soils (a) and (b) were sieved through a 2 mm stainless steel mesh and samples despatched to the Scottish Agricultural College for measurement of pH, organic matter content, particle size distribution and cation exchange capacity. Soils (c) and (d) were similarly sieved and characterised by the Scottish Agricultural College prior to arrival at IRI.
PROPERTIES
- pH: sand: 8.2
loamy sand: 4.7
loam: 7.0
clay loam: 5.9
- Organic matter (%): sand: 0.10
loamy sand: 2.60
loam: 1.97
clay loam: 5.20
- % sand: sand: 96.8
loamy sand: 86.3
loam: 45.6
clay loam: 38.9
- % silt: sand: 1.4
loamy sand: 3.6
loam: 29.5
clay loam: 28.8
- % clay: sand: 1.8
loamy sand: 10.1
loam: 24.8
clay loam: 32.2 - Key result
- Type:
- Koc
- Value:
- 136.06
- Remarks on result:
- other: geo mean for adsorption in all four soil types
- Type:
- Koc
- Value:
- > 388.3 - < 1 416
- Remarks on result:
- other: Soil 1: sand
- Type:
- Koc
- Value:
- > 46.74 - < 61.97
- Remarks on result:
- other: Soil 2: loamy sand
- Type:
- Koc
- Value:
- > 170.5 - < 306
- Remarks on result:
- other: Soil 3: loam
- Type:
- Koc
- Value:
- > 36.82 - < 41.31
- Remarks on result:
- other: Soil 4: clay loam
- Recovery of test material:
- Total recoveries of radioactivity from solution and soil were 91.71 - 97.11 % (mean values) for the sand, loamy sand and clay loam soils (excluding the sand at the lowest concentration which gave a lower recovery of 88.77 %). Lower mean total recoveries (78.46 - 88.26 %) were obtained for the loam soil.
- Transformation products:
- yes
- No.:
- #1
- No.:
- #2
- Details on results (Batch equilibrium method):
- - The test material was instable under test conditions and the observed degradation was extensive and varied in the presence of the 4 soil types.
- Lower adsorption of radioactivity was observed in the clay loam, the soil with the highest organic clay content, and therefore, the greatest potential adsorptive capacity. This might be explained by the presence, in the more alkaline loam soil, of the relative non-polar products (A, B) which
might be potentially more adsorptive than the relative polar conversion product (C) formed in the more acidic clay loam soil.
Reference
Description of key information
Adsorption to solid soil phase is not expected.
Key value for chemical safety assessment
Additional information
Adsorption of 14C-Bronopol onto and desorption from four different soil types was investigated (Jackson, 1992), according to US EPA Pesticide Assessment Guidelines, Subdivision N, Paragraph OPP 163-1. The results indicated that highest adsorption was observed in loam. Lower adsorption was observed in clay loam, loamy sand and sand. From the Kaoc values of the four different soil types, a Koc of 136.06 L/kg was calculated for Bronopol. According to the classification developed by FAO (2000) and recommended by US-EPA for the mobility in soil, Bronopol is considered as moderately mobile.
Additionally, the adsorption of 14C-Bronopol onto and desorption from four different soil types was investigated according to US EPA Pesticide Assessment Guidelines, Subdivision N, Paragraph OPP 163 -1 [The Boots Company 1992].
The results indicated that highest adsorption was observed in loam (< 26 %). Lower adsorption was observed in clay loam (< 25 %), loamy sand (< 13 %) and sand (< 8 %). Moreover, the test material was instable under test conditions and the observed degradation varied in the four soil types.
Adsorption of Bronopol and/or its degradation products was correlated to the soil pH. Higher adsorption was observed in alkaline soil (loam) than in acidic soil (clay loam) due to differences in the degradation pathway of Bronopol.
In fact, in the more alkaline loam soil, relatively non-polar degradation products (such as 2 -bromo-2 -nitroethanol) were observed which might be potentially more adsorptive than the relatively polar product (such as tris-(hydroxyl-ethyl)-nitromethane) formed in the more acidic clay loam soil.
Conclusively, adsorption to soil differs among the various soil types, however, the adsorption potential of Bronopol is generally low, indicating no obvious risk to the soil compartment.
Additionally, the Koc has been estimated by QSAR estimation using KOCWIN V.2.01, which is integrated in Epi Suite v4.11. A Koc of 1 was estimated using the MCI method. This finding supports the results of the experimental study that stated out that bronopol is unlikely to adsorb to the solid phase.
The Koc of bronopol is estimated as 5, using a water solubility of 2.0E+5 mg/L and a regression-derived equation [HSDB 2009]. This estimated Koc value suggests that bronopol is expected to have very high mobility in soil.
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